Kaijun Wang,
Qifan Mao,
Weimin Fei,
Lingxin Kong,
Xiaoyan Cao and
Zhenggui Gu*
Jiangsu Provincial Key Laboratory of Materials Cycling and Pollution Control, Nanjing Normal Univesity, Nanjing, Jiangsu 210023, China. E-mail: 07160@njnu.edu.cn
First published on 23rd February 2021
Layered double hydroxides are a promising platform material which can be combined with a variety of active species based on their characteristic features. Silicon@P123-templated Ce-doped layered double hydroxide (SiO2@CeMgAl-LDH(P123)) composites were synthesized via a facile in situ co-precipitation method, and characterized by TEM, X-ray diffraction, FTIR, XPS, CO2-, etc. in detail. Meanwhile, the calcined powder (SiO2@CeMgAl-LDO(P123)) possessed an excellent core–shell structure and a high surface area inherited from the LDH structure, which led to an outstanding catalytic activity (99.7% conversion of propylene oxide, 92.4% selectivity of propylene glycol methyl ether) under mild reaction conditions (120 °C). Cerium oxide provides a large number of oxygen vacancies and significantly improves the medium basic strength of the material, which facilitates the selective ring-opening of PO. Furthermore, the introduction and removal of P123 make the cerium oxide uniformly dispersed on the LDH layers, providing more reaction sites for the reaction of methanol and propylene oxide. The core–shell structure prepared by the in situ co-precipitation method could solve the shortcomings of agglomeration of layered double hydroxides and prolong the catalytic life evidently.
Although traditional solid base catalysts such as NaOH and KOH have good catalytic activity in similar alkoxylation reactions, such homogeneous and highly corrosive substances do great harm to industrial equipment and increase the difficulty of product refining. Recent researches of alcohol ether synthesis took ionic liquids5 and zeolitic imidazolate framework (ZIF-8)6 as important research objects. These new types of catalysts can achieve a high PO conversion rate with a relatively small amount of use, but they become a stumbling block in the product purification process. When used in the actual production process, the above catalysts are difficult to achieve the expected results. Heterogeneous catalysts are widely used in the synthesis of chemical products. They reduce the corrosion of equipment and the difficulty of product refining. Moreover, most of the heterogeneous catalysts have the advantages of simple preparation, controllable morphology and long catalytic life. It is the main trend of the development of chemical industry and one of the important ways to realize green chemical process.
In recent ten years, there have been a lot of reports on the synthesis of alcohol ether with heterogeneous solid base catalysts. Timofeeva prepared Al-pillared interlayered clays (Al-PILCs)7 and Zr,Al-pillared clays through the intercalation of Al- and Zr-polyoxocations into layered aluminosilicates with various textural properties and chemical compositions8 to explore the synthesis process of alcohol ethers. The catalytic performance of these materials was investigated in the synthesis of PGME. 0.4% Zr Al-MMNO3−K got a certain catalytic activity at 60 °C that conversion of PO was 71% and selectivity towards to PGME was 66%. The research found that the increase of Zr content was beneficial to decrease the selectivity of PGME, which was the result of a change in the nature of acid–base sites. The highest conversion and selectivity toward PGME were observed in the presence of materials with medium-strength basic sites, because high-strength basic sites can lead to a strong stabilization of methoxide and propylene-like species on the surface of the solid. Liu9 combined KF with La2O3-SBA-15 at low temperature to form ordered microstructure on the solid surface and generate superbase sites. The conversion of propylene oxide was 93%, and the selectivity of 1-methoxy-2-propanol was 93%. For the solid base catalyst used in this system, the higher specific surface area and the medium strong base strength can promote the yield of PGME obviously.10 Recently, for another piece of research, Timofeeva11 found that the catalytic properties of AM-4 could be adjusted by treatment with 0.0625–0.25 M HNO3. Increasing the concentration of HNO3 led to a decrease in basicity, which played a critical role in the reaction rate and the selectivity towards PGME. Their activity depended on the type of active sites, which is controlled by acid concentration. In a word, the more active sites with moderate and strong base strength and larger specific surface area are more conducive to the formation of secondary hydroxy alcohol ether.
The LDH structure is based on M(OH)6 octahedral units sharing edges in order to build M(OH)2 brucite-like layer.12 LDH plays an important role in the field of industrial catalysis. This is not only its special layer structure and ion exchange properties, but also it can be used as a carrier or an active component. This feature greatly expands the possibility of material topography modification. Therefore, in recent years, LDH-based multi-level structural composite materials have become the focus of attention.13–16 The metal components in the hydrotalcite laminate can be flexibly adjusted, so a wide variety of hydrotalcite-like catalysts can be designed for different reaction systems.17–19 Cerium is a rare earth element with the highest abundance. The crystal of CeO2 has the structure of cubic fluorite with primary characteristic surfaces of (111), (110) and (100). Due to the differences in the packing of atoms in bulk structure and certainly at surface, the interaction forces between the surfaces and the reactants would be different.20,21 The specific surface area, dispersion of active species, oxygen cavity defect and lattice oxygen fluidity of CeO2 can be changed by metal doped CeO2 and the interaction between metal and CeO2. Therefore, cerium based composite metal oxides have been widely used in the field of catalysis.22–24 Recently, incorporation of cerium oxide based nanostructured materials into layered double hydroxide to form composite material is another burning topic of research interest.25,26 Core–shell nanoparticles (CSNs) are a class of nanostructured materials that have recently received increased attention owing to their interesting properties and broad range of applications in catalysis, biology, materials chemistry and sensors.27
In our previous work, we have explored how to increase the specific surface area of the catalyst while ensuring the basic strength. We proved that the core–shell functional materials with specific morphology can be prepared by certain methods.28 We found that MgAl-LDH supported on SiO2 surface by in situ coprecipitation method can form core–shell materials with composite shell distribution in transverse and longitudinal directions. After calcination, the composite structure still maintains a certain integrity, and solves the problem that LDH is easy to agglomerate. At the same time, it shows ideal catalytic activity in fixed bed reactor.
Taking into consideration the above discussion, we report herein a novel SiO2@CeMgAl-LDH nanocatalyst, which was easily fabricated by the in situ coprecipitation of the CeMgAl-LDH anchored on the surface of amorphous SiO2 sphere. The template agent P123 is introduced in the material and removed by calcination for further treatment. The obtained material (SiO2@CeMgAl-LDO(P123)) was fully characterized and its catalytic activity was evaluated in the synthesis of PGME (Fig. 1). The catalytic performances of the as-prepared samples were correlated with the observed structural evolution of the catalysts. More importantly, this work could provide some directions and perspectives for the preparation of stable core–shell structure catalysts.
Fig. 2 TEM images of samples (a, b and b′) CeMgAl-LDO, (c, d and d′) SiO2@CeMgAl-LDH(P123), (e, f and f′) SiO2@CeMgAl-LDO(P123). |
The crystal structure of the as-prepared materials was confirmed by XRD analysis (Fig. 3). The CeMgAl-LDH and CeMgAl-LDH(P123) samples exhibit the characteristic diffraction peak of LDHs, indicating that Ce-doping and P123 addition does not destroy the layered structure of LDHs. Ce prefers to be located in the interlayer gallery of LDH as agglomerated cerium oxide species due to its high ionic radius (0.102 nm). After calcination, CeMgAl-LDO is mainly composed of amorphous Al2O3, MgO and CeO2. Peaks at 28.7°, 33.2°, 47.7° and 56.6° are corresponding to the (111), (200), (220), (311) planes of Fluorite CeO2 (JCPDS PDF#78-0694). MgO may gradually enter the CeO2 lattice to form a new solid solution structure. Moreover, there is no obvious diffraction peak of heterophase species in the whole XRD spectrum of CeMgAl-LDO, which shows that the metal oxides prepared by nucleation crystallization isolation method have pure crystal phase composition. The XRD patterns of SiO2@CeMgAl-LDH(P123) and SiO2@CeMgAl-LDO(P123) both show an LDH/LDO-originated diffraction pattern which confirmed the formation of the LDH/LDO on the silica sphere. The intensity of LDH/LDO originated peaks decreased due to the coexistence of amorphous SiO2. It was reported that Si–O–Mg and Si–O–Al bonds on the SiO2 surface deeply affected reduction of the crystallite size not only in the stacking direction but also in the plane direction.29
The FT-IR spectra are shown in Fig. 4. The peaks located in the 3000–3500 cm−1 region can be ascribed to the characteristic absorption bands of O–H attached to the metal cation bonds in the hydroxide layer and stretching vibration of interlayer water molecules. The width and relative strength of –OH in LDO decreased significantly due to hydroxyl removal caused by the calcination process. The bending vibration of interlayer water molecules are found at 1650 cm−1. Similar to the change in the –OH vibration peak, the absorption peak of LDO here basically disappears as water is removed between layers of the roasting process. A new peak appears at around 1092 cm−1 which could be supposed to the stretching vibrations of Si–O–Si and Si–O–H, indicating that SiO2 spheres are coated by the LDH platelets successfully in core–shell composites. The peak between 500 and 750 cm−1 can be assigned to the stretching vibrational mode of the Ce–O bonds.30 The peaks at 2932 and 2878 cm−1 are attributed to the alkyl stretching vibrations, both of which indicate the presence of P123 in as-synthesized materials.31 The FT-IR spectra indicated that the CeMgAl-LDHs/LDOs were involved on the surface of SiO2.
It is known that calcined LDHs, layered double oxides (LDOs), are useful intermediates for functionalised LDHs and that their tuneable acid/base properties can be utilised in catalytic applications.32 The TGA-DTG curves of samples are shown in Fig. 5. Compared to Mg–Al LDH, all the samples show a similar thermal behavior as follow: (1) in the temperature range 70–190 °C, loosely held interlayer water is lost; (2) in the temperature range 190–280 °C, the OH– group bonded with Al3+ is lost; (3) in the temperature range 280–450 °C, the OH– group bonded with Mg2+ is lost; (4) the weight of the three composites tends to be stable after 500 °C. The introduction of P123 makes the three weightlessness temperatures shift to high temperature. This is due to the hydrogen bonding between P123 and OH− or H2O, so higher energy requirements put forward in the process of chemical bond transformation.
The X-ray photoelectron spectroscopy (XPS) was used to study the oxidation state of the surface elements in SiO2@CeMgAl-LDO(P123), and SiO2@CeMgAl-LDH(P123). The Ce 3d, Mg 1s, and O 1s regions of the spectra are shown in Fig. 6b–d. The binding energy peaks at 1301 and 117 eV can be attributed to Mg 1s and Al 2s, respectively. The HXPS spectra of Ce 3d before and after samples being calcined indicate the presence of the mixed valence Ce3+ and Ce4+ states. The main peaks of Ce3+ 3d3/2 and Ce3+ 3d5/2 are shown at the bending energy of 990 eV and 882 eV. One additional peak at 907.6 eV is also attributed to the Ce 3p3d3/2 states. The peaks of Ce 4p are found at the binding energies of 916.5 eV.32–34 It shows that cerium exists in similar form in both materials, but the relative content of some Ce4+ increases obviously after calcination. More importantly, it is beneficial for Ce3+ to lose an electron to be oxidized to Ce4+, improving the lattice oxygen defects and the redox transformation between Ce3+ and Ce4+.35 The O 1s binding energy peak appeared at 529 eV in SiO2@CeMgAl-LDO(P123) was assigned to Ce–O, peak at 531 eV with oxygen vacancies of Ce3+ in CeO2 and surface oxygen species in the layered structure of LDH/LDO.
The specific BET surface area and pore volumes of CeMgAl-LDO, and SiO2@CeMgAl-LDO(P123) are shown in Fig. 7, S2† and Table 1. It can be easily found that SiO2@CeMgAl-LDO(P123) showed much higher specific BET surface area (358.71 m2 g−1) and larger pore volumes (1.13 cm3 g−1) compared with CeMgAl-LDO (144.94 m2 g−1; 0.72 cm3 g−1). As can be seen from Fig. 7, nitrogen adsorption–desorption isotherms of CeMgAl-LDO, and SiO2@CeMgAl-LDO(P123) both exhibit intermediate isotherms between type II (absence of a plateau at high P/P0) and type IV (low N2 adsorption at low P/P0), with a hysteresis loop in the relative pressure range of 0.4 to 1.0, indicating the presence of capillary condensation in the mesopore structure. According to the IUPAC classification, interestingly, these two samples present a mixture hysteresis loop of H2 and H3 types with an abrupt closure at a relative pressure of 0.45 due to the tensile strength effect, suggesting the presence of slit-shaped and ink-bottle pores in the mesopore network associated with the aggregates of plate-like particles.36 In the adsorption desorption curve of SiO2@CeMgAl-LDO(P123), the hysteresis loop is larger, which shows that there are more complex hole structures. During the formation of the nuclear shell structure, the shell structure is relatively complex, with different forms such as horizontal fit, vertical growth and mixed construction. Due to the pore forming process of P123, the pore structure becomes more complex.
Catalyst | BET surface (m2 g−1) | CO2 uptake (cm3 g−1 STP) | ||
---|---|---|---|---|
W | M | S | ||
a W, weak basic site; M, medium basic sites; S, strong basic sites, cm3 g−1 STP. | ||||
MgAl-LDO | 167.89 | 5.24 | 40.81 | 0.36 |
CeMgAl-LDO | 136.59 | 2.75 | 103.43 | 7.44 |
CeMgAl-LDO(P123) | 144.94 | 4.03 | 137.87 | 12.99 |
SiO2@CeMgAl-LDO | 342.11 | 4.27 | 129.08 | 13.05 |
SiO2@CeMgAl-LDO(P123) | 358.71 | 3.66 | 145.62 | 13.59 |
The CO2-TPD was used to analyze the effect of the strength and number of basic sites on the surfaces of the catalysts and the results were presented in Fig. 8 and Table 1. It could be seen that all the catalysts displayed CO2 desorption peaks at a similar temperature range of 200–400 °C and 500–600 °C. The low-temperature desorption peaks centered at 270 °C could be contributed to weakly CO2 chemisorbed by aluminum hydroxy and MgO.37 The peaks located at about 325 °C could be assigned to the medium basic sites derived from the oxygen vacancies formed during the doping of cerium in MgAl-LDO based composite. Combined with the results of specific surface area measurement, the core–shell structure has more complete stereoscopic structure and provides more alkaline sites at the same time. Moreover, the material with P123 template has the strongest total alkali content and strong alkali center strength.
Catalyst | Experimental conditions | Conversion of PO (%) | Selectivity of PGME (%) | |||
---|---|---|---|---|---|---|
Catalyst (wt%) | Me/PO (mol mol−1) | T (°C) | Time (h) | |||
— | — | 4 | 120 | 8 | 21.3 | 58.2 |
SiO2 | 1 | 4 | 120 | 8 | 23.8 | 74.2 |
Al2O3 | 1 | 4 | 120 | 8 | 60.3 | 70.6 |
Mg3Al-LDO | 1 | 4 | 120 | 8 | 58.5 | 83.8 |
*7Al-MMR | 3 | 8 | 60 | 6 | 98.7 | 61.2 |
*912%KF/La2O3-SBA-15 | 1 | 5 | 125 | 4 | 93.0 | 91.0 |
*40ZIF-8 | 1.85 | 8 | 120 | 5 | 55.4 | 93.8 |
*40MAF-5 | 1.85 | 8 | 110 | 5 | 90.3 | 92.6 |
*11AM-4 | 1.8 | 5 | 110 | 5 | 88.4 | 92.3 |
*62.9%ZIF-8/Nafen | 1.6 | 5 | 120 | 5 | 84.1 | 86.3 |
Ce0.33Mg2Al1-LDO | 2 | 4 | 120 | 8 | 96.7 | 89.6 |
Ce0.33Mg2Al1-LDO(P123) | 2 | 4 | 120 | 8 | 97.6 | 89.8 |
Ce1Mg3Al1-LDO(P123) | 2 | 4 | 120 | 8 | 97.8 | 86.3 |
SiO2@Ce0.33Mg2Al1-LDO | 2 | 4 | 120 | 8 | 97.8 | 91.6 |
SiO2@Ce0.33Mg2A1-LDO(P123) | 2 | 4 | 120 | 8 | 99.7 | 92.4 |
SiO2@Ce1Mg3A1-LDO(P123) | 2 | 4 | 120 | 8 | 90.3 | 86.5 |
SiO2@Ce0.3Mg3Al1-LDO(P123) | 2 | 4 | 120 | 8 | 94.6 | 90.4 |
SiO2@Ce0.05Mg3Al1-LDO(P123) | 2 | 4 | 120 | 8 | 88.3 | 89.6 |
The mechanism of the reaction on different single component basic catalysts has been discussed.38,39 The moderate basic sites of Lewis-acid–Bronsted-base pairs and isolated surface O2− ions were appropriate to dissociate methanol to methoxide and had the ability to abstract a proton from propylene oxide.
In the present work, the catalytic performance of the as-prepared core–shell composites was tested in the synthesis of propylene glycol methyl ether from methanol and PO. Table 2 shows that the conversion of PO in the presence of SiO2@Ce0.33Mg2Al1-LDO(P123) was 99.7%, a relatively high level among the prepared and reported catalysts. Although ZIF-8 has the best selectivity for propylene glycol monomethyl ether, it is difficult to apply ZIF-8 in the actual production process considering the stability and cost of the catalyst. The selectivity towards PGME was higher in the presence of SiO2@Ce0.33Mg2Al1-LDO(P123) (92.4%) than other heterogeneous catalysts. Probably, this phenomenon is related to the difference in the strength of the moderate basic sites. The activity of CeMgAl-LDO is greatly higher than those of the MgAl-LDO or pure Al2O3 sample, indicating that the introduction of Ce ions into the Mg–Al catalysts can significantly enhance the catalytic performance. The CeO2 grains were uniformly distributed on the LDO structure and interacted strongly with Mg–O–Al bonds. This strong interaction leads to the formation of coordinately unsaturated surface Ce3+ cations. Besides, the introduction of Ce cations in Mg–Al mixed oxides can modify the acid–base properties of the mixed oxides. Some studies have shown that the aggregation of CeO2 grains can weaken the catalytic performance of the catalyst. Therefore, the specific gravity of Ce in the composite should not be too large, and the agglomeration of CeO2 should be avoided. According to TEM analysis, when P123 was introduced, CeO2 was well dispersed, which was consistent with the phenomenon that the catalytic performance of P123 modified materials was significantly better than that of unmodified materials. According to the literature,41,42 the strength of basic sites determines the reaction rate and the isomer selectivity toward PGME. Our experimental data also point out that strong basic sites lead to a decrease in the selectivity of PGME. It is reported that a high strength of strong basic sites can lead to a strong stabilization of methoxide and propylene-like species which formed as intermediates on the surface of the solid and, in this way, hinder the process of reaction.8
The element ratio of the catalyst and the reaction conditions were also studied. In Table 2, we investigated the element ratio of the catalyst and found that SiO2@Ce0.33Mg2A1-LDO(P123) has the best catalytic activity. When the amount of Ce increased, although the conversion of PO did not decrease, the selectivity of PGME decreased significantly. In the TEM image analysis (Fig. S1†) of Ce1Mg3A1-LDO(P123), more complex lattice fringes and crystal structure can be found, and the agglomeration of CeO2 is serious. When the specific gravity of the crystal plane which plays the main catalytic role decreases, the selectivity will be affected negatively. Then in the exploration of reaction conditions, too long reaction time and high temperature will affect the selectivity of PGME. This is because that under a certain proportion or environmental conditions, PGME and PO will polymerize to form polypropylene glycol monomethyl ether with different degrees of polymerization, which will seriously affect the quality of the product. After single factor optimization (Fig. S3†), the conversion of PO reaches 99.7% and selectivity of PGME reaches 92.4% at a molar ration Me/PO 4:1 and 120 °C for 8 h via 1 wt% SiO2@Ce0.33Mg2A1-LDO(P123).
The catalyst was separated by filtration after the first test, washed with methanol, dried in air and activated at 550 °C for 6 h, and then reused for the next run under the same conditions. The results are depicted in Fig. 9. As shown in the figure, the catalytic activity of the reused catalyst was slightly affected at the fifth run, exhibiting >93.0% conversion and retaining 87.0% selectivity to PGME. These results imply that the catalyst can be efficiently recovered and recycled.
Fig. 9 Recycling test in reaction between propylene oxide and methanol in the presence of SiO2@Ce0.33Mg2Al1-LDO(P123). |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/d1ra00227a |
This journal is © The Royal Society of Chemistry 2021 |